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ENVIRONMENTAL CONSEQUENCES in rocky mountain coniferous ...

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INFLUENCE OF HARVESTING AND RESIDUES ON<br />

FUELS AND FIRE MANAGEMENT<br />

Timber harvest<strong>in</strong>g produces frrest fuels with fire behavior potentials of<br />

great concern to land managers. Fires <strong>in</strong>volv<strong>in</strong>g slash fuels can be particularly<br />

difficult to control, generate high costs of suppression and threaten resource<br />

values. Fuel quantities from harvest<strong>in</strong>g vary substantially and can be excessive,<br />

depend<strong>in</strong>g on volumes cut and methods of harvest (Howard 1973; Benson and Johnston<br />

1976). Util ization standards and methods of skidd<strong>in</strong>g offer the manager opportunities<br />

to modify fuel hazards, because they <strong>in</strong>fluence fuel load<strong>in</strong>g, size distribution,<br />

conti nu5 ty, and compactness.<br />

Little has been documented on the extent to which harvest<strong>in</strong>g methods can<br />

alter fuel characteristics and fire potentials. However, techniques developed<br />

over the past few years for measur<strong>in</strong>g and predict<strong>in</strong>g fuels and flre behavior have<br />

made it possible to appraise slash fuels. This paper describes how different<br />

harvest<strong>in</strong>g methods altered fuels and fire potential on two study areas and discusses<br />

how managers can appraise fuels on any cutt<strong>in</strong>g area before slash is created.<br />

CASE STUDIES AT UNION PASS AND CORAM<br />

Study Procedures<br />

Effects of harvest<strong>in</strong>g on fuel and fire behavior potential were evaluated at<br />

two locations: Union Pass on the Bridger-Teton National Forest <strong>in</strong> Wyom<strong>in</strong>g, and<br />

Coram Experimental Forest on the Flathead National Forest <strong>in</strong> Montana. Forest<br />

conditions and study designs were different.<br />

UNION PASS<br />

Two mature, even-aged lodgepole p<strong>in</strong>e stands were studied. In each stand, two<br />

20-acre harvest<strong>in</strong>g units were established. One unit was clearcut to "conventional I'<br />

util izatian standards, the other to utilization standards that were called "near-<br />

completeI1 . On both the conventional and near-compl ete harvest<strong>in</strong>g units a1 1 sound<br />

trees to a merchantable top diameter of 6 <strong>in</strong>ches were removed. In addition, on<br />

the near-complete unlts chips were produced from: (a) tops of all merchantable<br />

trees; (b) a ll rema<strong>in</strong><strong>in</strong>g live and dead sound stand<strong>in</strong>g trees with a d.b,h. of 3<br />

<strong>in</strong>ches or larger; and (c) a11 material rema<strong>in</strong><strong>in</strong>g on the ground that was more than<br />

6 <strong>in</strong>ches <strong>in</strong> diameter at the larger end, more than 6 feet long, and sound enough to<br />

permit skidd<strong>in</strong>g. On the conventional units, trees were limbed and bucked where<br />

felled, then skidded by crawler tractor to the land<strong>in</strong>g. On the near-complete<br />

units, trees were felled and then bunched and skidded to a central po<strong>in</strong>t where the<br />

sawlog material was removed. The rema<strong>in</strong><strong>in</strong>g top material was then skidded to the<br />

chipper.

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